Microplastic Contamination in Chinnamuttom Coast Seawaters: An Investigative Study | InformativeBD

Microplastic footprints in the seawaters of Chinnamuttom Coast, Kanyakumari: An investigation

N. Sivalingitha, Jeni Chandar Padua, P. C. Jeba Preethi Jansi, and J. Agnel, from the different institute of India. wrote a Research Article about, Microplastic Contamination in Chinnamuttom Coast Seawaters: An Investigative Study. Entitled, Microplastic footprints in the seawaters of Chinnamuttom Coast, Kanyakumari: An investigation. This research paper published by the Journal of Biodiversity and Environmental Sciences (JBES). an open access scholarly research journal on Biodiversity. under the affiliation of the International Network For Natural Sciences| INNSpub. an open access multidisciplinary research journal publisher.

Abstract

The study examines the microplastics contamination in marine waters along the Chinnamuttom coast. Density separation, filtration and sieving methods are employed to collect microplastics. The morphology, shape and colour of the microplastics collected were determined through visual analysis using microscopic identification. Microplastics were characterized using Scanning Electron Microscopy (SEM) and FT-Raman spectroscopic investigations. The study revealed the presence of microplastics smaller than 5 mm. Approximately 70 mg of dried microplastics were obtained per 5 liters of water. The microplastics primarily consisted of fibers, pellets, and fragments, exhibiting a range of colours including orange pellets, black filaments and fibers in blue, pink, white and purple hues. Particles as small as 20 µm in diameter were detected using scanning electron microscopy, while Raman spectroscopy identified polymers such as polystyrene and nylon through their distinctive vibrational peaks, confirming the presence of bonds like C-H, aldehyde and C=C. The extensive pollution underscores critical ecological issues facing the Chinnamuttom coastal environment, potentially intensified by nearby fishing and tourism practices. The results emphasize the critical necessity for approaches aimed at reducing microplastic contamination in these aquatic environments to safeguard marine biodiversity and the overall health of ecosystems.

Submit your article to JBES Journal

Introduction

Microplastics are defined as plastic fragments or particles that measure less than 5 mm in diameter, resulting from the breakdown of larger plastic materials (Pellini et al., 2018). 

Microplastics are widespread in the environment, particularly in marine settings, as a result of hydrodynamic processes and transportation via wind and ocean currents. Large ocean gyres such as the Pacific, Atlantic, and Indian Oceans, along with polar regions and the equator, host them, stretching from coastal areas to the open seas (Galgani et al., 2013). Microplastics are characterized by a variety of morphologies, including foils, foams, fibers, granules, fragments, and microbeads (Klein et al., 2018).

Microplastics can be classified into two categories based on their original dimensions. Municipal effluent could directly introduce industrially produced particulates and powders, originally designed as plastic microbeads, into the ocean as primary microplastics (Cole et al., 2011). Various physical, biological, and chemical processes fragment and degrade substantial plastic pieces, resulting in smaller particles known as secondary microplastics that may enter marine ecosystems (Arias-Villamizar et al., 2018).

Secondary microplastics refer to the fragmentation of larger plastic materials resulting from various forms of degradation, including biological processes involving microbial species, photodegradation caused by solar ultraviolet radiation, and mechanical abrasion due to wave action. Mechanical damage, photodegradation, and oxidative degradation are all mechanisms that degrade fragile polymers into microplastics in the ocean (Wagner et al., 2014).

A diverse array of sources contributes to microplastic pollution in the marine environment, broadly classified as inland-based, sea-based, and air-based (Andrady, 2011; Browne et al., 2011). According to Lebreton et al. (2017), rivers are the most critical conduits for the transportation of microplastics from inland regions to the ocean. The terrestrial environment is the source of approximately 80% of the plastic debris in the ocean (Andrady, 2011; Mani et al., 2015). Rivers transport plastic debris from urban drainage systems and sewage effluents to the sea, while coastal tourists immediately dispose of their plastic garbage in the environment (Andrady, 2011). Marine sources come from fisheries, maritime transport, and offshore industry (Bell et al., 2017). Plastic debris may end up in the waterways due to broken or lost fishing or aquaculture gear (Law and Thompson, 2014). 

Due to their increased bioavailability and potential negative effects on marine ecosystems over the long term, microplastics are expected to garner significant public attention in the next few years (Velzeboer et al., 2014). Although the exact nature of microplastics (MPs) and the harm they do to marine life is still largely unknown, there is mounting evidence that these contaminants pose a serious threat to marine ecosystems (Chen et al., 2017). Measures and initiatives are necessary to address the issues arising from microplastics and enhance plastic waste management. Hence, the present study aims to classify the microplastics based on their shape, size, colour and to evaluate the chemical composition of microplastics found in the seawater of the Chinnamuttom coast.

Reference

Andrady AL. 2011. Microplastics in the marine environment. Marine Pollution Bulletin 62, 1596–1605.

Araujo CF, Nolasco MM, Ribeiro AM, Ribeiro-Claro PJ. 2018. Identification of microplastics using Raman spectroscopy: Latest developments and future prospects. Water Research 142, 426–440.

Arias AH, Ronda AC, Oliva AL, Marcovecchio JE. 2019. Evidence of microplastic ingestion by fish from the Bahía Blanca estuary in Argentina, South America. Bulletin of Environmental Contamination and Toxicology 102, 750–756.

Arias-Villamizar CA, Vázquez-Morillas A. 2018. Degradation of conventional and oxodegradable high-density polyethylene in tropical aqueous and outdoor environments. Revista Internacional de Contaminación Ambiental 34, 137–147.

Becucci M, Mancini M, Campo R, Paris E. 2022. Microplastics in the Florence wastewater treatment plant studied by a continuous sampling method and Raman spectroscopy: A preliminary investigation. Science of The Total Environment 808, 152025.

Bell JD, Watson RA, Ye Y. 2017. Global fishing capacity and fishing effort from 1950 to 2012. Fish and Fisheries 18, 489–505.

Bobori DC, Dimitriadi A, Feidantsis K, Samiotaki A, Fafouti D, Sampsonidis I, Kalogiannis S, Kastrinaki G, Lambropoulou DA, Kyzas GZ, Koumoundouros G. 2022. Differentiation in the expression of toxic effects of polyethylene microplastics on two freshwater fish species: Size matters. Science of the Total Environment 830, 154603.

Browne MA, Crump P, Niven SJ, Teuten E, Tonkin A, Galloway T, Thompson R. 2011. Accumulation of microplastic on shorelines worldwide: sources and sinks. Environmental Science & Technology 45, 9175–9179.

Chen Q, Yin D, Jia Y, Schiwy S, Legradi J, Yang S, Hollert H. 2017. Enhanced uptake of BPA in the presence of nanoplastics can lead to neurotoxic effects in adult zebrafish. Science of the Total Environment 609, 1312–1321.

Cole M, Lindeque P, Halsband C, Galloway TS. 2011. Microplastics as contaminants in the marine environment: a review. Marine Pollution Bulletin 62, 2588–2597.

Ding J, Jiang F, Li J, Wang Z, Sun C, Wang Z, Fu L, Ding NX, He C. 2019. Microplastics in the coral reef systems from Xisha Islands of South China Sea. Environmental Science & Technology 53, 8036–8046.

Galgani F, Hanke G, Werner SDVL, De Vrees L. 2013. Marine litter within the European marine strategy framework directive. ICES Journal of Marine Science 70, 1055–1064.

Gardon T, Paul-Pont I, Le Moullac G, Soyez C, Lagarde F, Huvet A. 2022. Cryogrinding and sieving techniques as challenges towards producing controlled size range microplastics for relevant ecotoxicological tests. Environmental Pollution (Barking, Essex: 1987), 315, 120383. https://doi.org/10.1016/j.envpol.2022.120383.

Hamed M, Martyniuk CJ, Lee JS, Shi H, Sayed AEDH. 2023. Distribution, abundance, and composition of microplastics in market fishes from the Red and Mediterranean seas in Egypt. Journal of Sea Research 194, 102407.

Klein S, Worch E, Knepper TP. 2015. Occurrence and spatial distribution of microplastics in river shore sediments of the Rhine-Main area in Germany. Environmental Science & Technology 49, 6070–6076.

Kooi M, Reisser J, Slat B, Ferrari FF, Schmid MS, Cunsolo S, Brambini R, Noble K, Sirks LA, Linders TE, Schoeneich-Argent RI. 2016. The effect of particle properties on the depth profile of buoyant plastics in the ocean. Scientific Reports 6, 33882.

Koongolla JB, Andrady AL, Kumara PTP, Gangabadage CS. 2018. Evidence of microplastics pollution in coastal beaches and waters in southern Sri Lanka. Marine Pollution Bulletin 137, 277–284.

Law KL, Thompson RC. 2014. Microplastics in the seas. Science 345, 144–145.

Lebreton LC, Van Der Zwet J, Damsteeg JW, Slat B, Andrady A, Reisser J. 2017. River plastic emissions to the world’s oceans. Nature Communications 8, 15611.

Li D. 2019. Research advance and countermeasures on marine microplastic pollution. Research of Environmental Sciences 32, 197–202.

Liu J, Zhang X, Du Z. 2020. Application of confocal laser Raman spectroscopy on marine sediment microplastics. Journal of Oceanology and Limnology 38, 1502–1516. https://doi.org/10.1007/s00343-020-0129-z.

Liu S, Jian M, Zhou L, Li W. 2019. Distribution and characteristics of microplastics in the sediments of Poyang Lake, China. Water Science and Technology 79, 1868–1877.

Mani T, Hauk A, Walter U, Burkhardt-Holm P. 2015. Microplastics profile along the Rhine River. Scientific Reports 5, 17988.

Melo-Agustín P, Kozak ER, de Jesús Perea-Flores M, Mendoza-Pérez JA. 2022. Identification of microplastics and associated contaminants using ultra high resolution microscopic and spectroscopic techniques. Science of the Total Environment 828, 154434.

Novotna K, Cermakova L, Pivokonska L, Cajthaml T, Pivokonsky M. 2019. Microplastics in drinking water treatment–current knowledge and research needs. Science of the Total Environment 667, 730–740.

Pellini G, Gomiero A, Fortibuoni T, Ferrà C, Grati F, Tassetti AN, Polidori P, Fabi G, Scarcella G. 2018. Characterization of microplastic litter in the gastrointestinal tract of Solea solea from the Adriatic Sea. Environmental Pollution 234, 943–952.

Razeghi N, Hamidian AH, Wu C. 2021. Microplastic sampling techniques in freshwaters and sediments: a review. Environmental Chemistry Letters 19, 4225–4252. https://doi.org/10.1007/s10311-021-01227-6.

Sul JAI, Costa MF. 2014. The present and future of microplastic pollution in the marine environment. Environmental Pollution 185, 352–364.

Velzeboer I, Kwadijk CJAF, Koelmans AA. 2014. Strong sorption of PCBs to nanoplastics, microplastics, carbon nanotubes, and fullerenes. Environmental Science & Technology 48, 4869–4876.

Wagner M, Scherer C, Alvarez-Muñoz D, Brennholt N, Bourrain X, Buchinger S, Fries E, Grosbois C, Klasmeier J, Marti T, Rodriguez-Mozaz S. 2014. Microplastics in freshwater ecosystems: what we know and what we need to know. Environmental Sciences Europe 26, 1–9.

Wright SL, Kelly FJ. 2017. Plastic and human health: A micro issue. Environmental Science & Technology 51, 6634–6647.

SourceMicroplastic footprints in the seawaters of Chinnamuttom Coast, Kanyakumari: An investigation  

0 comments: